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. 2010 Jun 8;118(10):1382–1388. doi: 10.1289/ehp.1001939

Table 3.

Summary of linear regression models evaluated for human WNV incidence rates and WNV-positive corvid death ratios per census tract in Atlanta, 2001–2007.a

2000 U.S. Census
Response variable Modelb Mean distance to CSO (m) Mean distance to catch basin (m) Mean tree cover (%) Mean elevation (m) Percent houses 1950s–1960s Median household income (U.S. dollars) No. dead corvids Constant AIC ΔAIC ωic
Human WNV incidence
 1 −6E–5** −0.0018 0.0276* −1E–5* −0.0362 3.60* 309.0 0.0 0.817
 2 −6E–5** 5E–5 −0.0012 −0.0018 0.0287* −2E–5* −0.032 4.13* 313.1 4.1 0.105
 3 −8E–5* 3E–5 −0.117* 2.65* 314.8 5.8 0.04
 4 0.0381* −2E–5* 3.58* 316.8 7.8 0.02
 5 −0.020* −0.0035 3.75* 316.9 7.9 0.02
 ∑ωi 9.7E–1c 0.0 0.02 0.0 0.94 9.2E–1 0.04

WNV-positive corvid death ratio
 1 −6E–4* 0.194* 0.1095 1.0E–5* 4.26* 707.0 0 0.913
 2 −6E–4* 2E–5 0.215* −0.0159 0.1023 −6.0E–5 10.46* 711.7 4.7 0.09
 3 0.186* 1.4E–4* 1.19 728.2 21.2 0.00
 4 0.172* −0.0017 4.83 728.4 21.4 0.00
 5 −3E–4 −1E–5 11.61* 739.9 32.9 0.00
 ∑ωi 1.0 0.0 1.0 0.0 0.0 9.1E–1
a

Results show the parameter estimates and p-values for each predictor; different models are ordered from best to worst.

b

Each candidate model included 455 observations. Numbers indicate the parameter estimate for each variable included in a given model. Dependent variables (human WNV incidence rates and WNV-positive corvid death ratios) were log10+1 transformed, whereas independent variables were estimated over each census tract.

c

Akaike weights, ωi = exp(−1/2 ΔAIC) / ∑exp((−1/2 ΔAIC).

c

After including variables with p < 0.07 in the estimation of ∑ωi. Without including marginally significant variables, the sum of Akaike weights drop to 0.04.

*

p < 0.05;

**

p < 0.07.